Hao Wu , Jia Zhou , Yucang Wang , Xinyi Jiao , Zheqi Pan , Yu Zhang , Jingjing Du , Zeqi Zhang , Longdan Ma , Dingjiang Chen
{"title":"中国东部典型流域磷长期营养轨迹探索(ELEMeNT-P)模型的修正","authors":"Hao Wu , Jia Zhou , Yucang Wang , Xinyi Jiao , Zheqi Pan , Yu Zhang , Jingjing Du , Zeqi Zhang , Longdan Ma , Dingjiang Chen","doi":"10.1016/j.jhydrol.2025.133718","DOIUrl":null,"url":null,"abstract":"<div><div>Excess anthropogenic phosphorus (P) inputs lead to the accumulation of legacy P in watersheds, which subsequently becomes a persistent source of P pollution to aquatic systems thereby hindering the effectiveness of water quality mitigation strategies. The ELEMeNT-P (Exploration of Long-tErM Nutrient Trajectories-Phosphorus) model is a process-based model for simulating legacy P dynamics that conceptualizes the hydrological and biogeochemical legacy components of P inputs to riverine export. However, ELEMeNT-P adopts a soil erosion loss equation originally designed for the Mediterranean region and ignores the threshold transition of soil P leaching that occurs following P sorption saturation, making it less applicable to other areas. Herein, we applied the Chinese soil loss equation to estimate soil erosion and an exponential function based on peak flow to calculate surface runoff P loss in a Chinses watershed. Further, a breakthrough curve was incorporated to characterize the rapid increase in soil P leaching once the soil P content exceeded a specified threshold. The modified ELEMeNT-P model was then evaluated for the Yongan watershed in eastern China to quantify legacy P dynamics over a 41-year period (1980–2020). The modified model improved the efficiency metrics for riverine P fluxes compared to the original model (R<sup>2</sup>: 0.94 vs. 0.79 and Nash-Sutcliffe Efficiency: 0.94 vs. 0.48). The P saturation ratio of 50 % for soils exceeded the threshold, indicating a high risk of P leaching, while Hedley P fractionation and soil total P test validated the model’s results in soil P type proportions and spatial distributions of legacy P (R<sup>2</sup> = 0.56). The results revealed that legacy P accumulation showed considerable spatial heterogeneity, with 40.0–504.9 kg P ha<sup>−1</sup> accumulated in soil and 26.7–41.5 kg P ha<sup>−1</sup> accumulated in groundwater. Riverine P flux mainly originated from legacy P pools (60.1 %, range: 21.5–90.3 %). The recovery time for depletion of the legacy P stock to the 1980 level via riverine export was 300 years, assuming total cessation of P inputs. Overall, the modified model was effective for determining the spatial and temporal distribution of legacy P within the watershed and therefore serves as an effective method to guide watershed P management.</div></div>","PeriodicalId":362,"journal":{"name":"Journal of Hydrology","volume":"661 ","pages":"Article 133718"},"PeriodicalIF":6.3000,"publicationDate":"2025-06-16","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Modification of Exploration of Long‐term Nutrient Trajectories for Phosphorus (ELEMeNT-P) model to quantify legacy phosphorus dynamics in a typical watershed of eastern China\",\"authors\":\"Hao Wu , Jia Zhou , Yucang Wang , Xinyi Jiao , Zheqi Pan , Yu Zhang , Jingjing Du , Zeqi Zhang , Longdan Ma , Dingjiang Chen\",\"doi\":\"10.1016/j.jhydrol.2025.133718\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<div><div>Excess anthropogenic phosphorus (P) inputs lead to the accumulation of legacy P in watersheds, which subsequently becomes a persistent source of P pollution to aquatic systems thereby hindering the effectiveness of water quality mitigation strategies. The ELEMeNT-P (Exploration of Long-tErM Nutrient Trajectories-Phosphorus) model is a process-based model for simulating legacy P dynamics that conceptualizes the hydrological and biogeochemical legacy components of P inputs to riverine export. However, ELEMeNT-P adopts a soil erosion loss equation originally designed for the Mediterranean region and ignores the threshold transition of soil P leaching that occurs following P sorption saturation, making it less applicable to other areas. Herein, we applied the Chinese soil loss equation to estimate soil erosion and an exponential function based on peak flow to calculate surface runoff P loss in a Chinses watershed. Further, a breakthrough curve was incorporated to characterize the rapid increase in soil P leaching once the soil P content exceeded a specified threshold. The modified ELEMeNT-P model was then evaluated for the Yongan watershed in eastern China to quantify legacy P dynamics over a 41-year period (1980–2020). The modified model improved the efficiency metrics for riverine P fluxes compared to the original model (R<sup>2</sup>: 0.94 vs. 0.79 and Nash-Sutcliffe Efficiency: 0.94 vs. 0.48). The P saturation ratio of 50 % for soils exceeded the threshold, indicating a high risk of P leaching, while Hedley P fractionation and soil total P test validated the model’s results in soil P type proportions and spatial distributions of legacy P (R<sup>2</sup> = 0.56). The results revealed that legacy P accumulation showed considerable spatial heterogeneity, with 40.0–504.9 kg P ha<sup>−1</sup> accumulated in soil and 26.7–41.5 kg P ha<sup>−1</sup> accumulated in groundwater. Riverine P flux mainly originated from legacy P pools (60.1 %, range: 21.5–90.3 %). The recovery time for depletion of the legacy P stock to the 1980 level via riverine export was 300 years, assuming total cessation of P inputs. Overall, the modified model was effective for determining the spatial and temporal distribution of legacy P within the watershed and therefore serves as an effective method to guide watershed P management.</div></div>\",\"PeriodicalId\":362,\"journal\":{\"name\":\"Journal of Hydrology\",\"volume\":\"661 \",\"pages\":\"Article 133718\"},\"PeriodicalIF\":6.3000,\"publicationDate\":\"2025-06-16\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Journal of Hydrology\",\"FirstCategoryId\":\"89\",\"ListUrlMain\":\"https://www.sciencedirect.com/science/article/pii/S002216942501056X\",\"RegionNum\":1,\"RegionCategory\":\"地球科学\",\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q1\",\"JCRName\":\"ENGINEERING, CIVIL\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Journal of Hydrology","FirstCategoryId":"89","ListUrlMain":"https://www.sciencedirect.com/science/article/pii/S002216942501056X","RegionNum":1,"RegionCategory":"地球科学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"ENGINEERING, CIVIL","Score":null,"Total":0}
引用次数: 0
摘要
过量的人为磷(P)输入导致流域遗留磷的积累,随后成为水生系统磷污染的持续来源,从而阻碍了水质缓解策略的有效性。ELEMeNT-P(探索长期营养轨迹-磷)模型是一个基于过程的模型,用于模拟遗留磷动力学,将磷输入到河流输出的水文和生物地球化学遗留成分概念化。但ELEMeNT-P采用了最初为地中海地区设计的土壤侵蚀损失方程,忽略了土壤磷吸附饱和后的淋溶阈值过渡,对其他地区的适用性较差。本文采用中国土壤流失方程估算土壤侵蚀,并采用基于峰值流量的指数函数计算中国流域地表径流磷损失。此外,引入突破曲线来表征土壤磷含量超过特定阈值后土壤磷淋溶的快速增加。利用改进的ELEMeNT-P模型对中国东部永安流域进行了评估,量化了41年(1980-2020年)的遗留P动态。与原始模型相比,改进后的模型提高了河流P通量的效率指标(R2: 0.94 vs. 0.79, Nash-Sutcliffe效率:0.94 vs. 0.48)。土壤磷饱和度达到50%,超过阈值,表明土壤磷淋溶风险较高,而Hedley磷分异和土壤全磷检验在土壤磷类型比例和遗留磷空间分布上验证了模型结果(R2 = 0.56)。结果表明,土壤中磷积累量为40.0 ~ 504.9 kg P ha−1,地下水中磷积累量为26.7 ~ 41.5 kg P ha−1。河流P通量主要来源于遗留P池(60.1%,范围21.5 ~ 90.3%)。假设完全停止磷输入,通过河流出口使遗留磷储量恢复到1980年水平的时间为300年。总体而言,修正后的模型能够有效地确定流域内遗留磷的时空分布,因此可以作为指导流域磷管理的有效方法。
Modification of Exploration of Long‐term Nutrient Trajectories for Phosphorus (ELEMeNT-P) model to quantify legacy phosphorus dynamics in a typical watershed of eastern China
Excess anthropogenic phosphorus (P) inputs lead to the accumulation of legacy P in watersheds, which subsequently becomes a persistent source of P pollution to aquatic systems thereby hindering the effectiveness of water quality mitigation strategies. The ELEMeNT-P (Exploration of Long-tErM Nutrient Trajectories-Phosphorus) model is a process-based model for simulating legacy P dynamics that conceptualizes the hydrological and biogeochemical legacy components of P inputs to riverine export. However, ELEMeNT-P adopts a soil erosion loss equation originally designed for the Mediterranean region and ignores the threshold transition of soil P leaching that occurs following P sorption saturation, making it less applicable to other areas. Herein, we applied the Chinese soil loss equation to estimate soil erosion and an exponential function based on peak flow to calculate surface runoff P loss in a Chinses watershed. Further, a breakthrough curve was incorporated to characterize the rapid increase in soil P leaching once the soil P content exceeded a specified threshold. The modified ELEMeNT-P model was then evaluated for the Yongan watershed in eastern China to quantify legacy P dynamics over a 41-year period (1980–2020). The modified model improved the efficiency metrics for riverine P fluxes compared to the original model (R2: 0.94 vs. 0.79 and Nash-Sutcliffe Efficiency: 0.94 vs. 0.48). The P saturation ratio of 50 % for soils exceeded the threshold, indicating a high risk of P leaching, while Hedley P fractionation and soil total P test validated the model’s results in soil P type proportions and spatial distributions of legacy P (R2 = 0.56). The results revealed that legacy P accumulation showed considerable spatial heterogeneity, with 40.0–504.9 kg P ha−1 accumulated in soil and 26.7–41.5 kg P ha−1 accumulated in groundwater. Riverine P flux mainly originated from legacy P pools (60.1 %, range: 21.5–90.3 %). The recovery time for depletion of the legacy P stock to the 1980 level via riverine export was 300 years, assuming total cessation of P inputs. Overall, the modified model was effective for determining the spatial and temporal distribution of legacy P within the watershed and therefore serves as an effective method to guide watershed P management.
期刊介绍:
The Journal of Hydrology publishes original research papers and comprehensive reviews in all the subfields of the hydrological sciences including water based management and policy issues that impact on economics and society. These comprise, but are not limited to the physical, chemical, biogeochemical, stochastic and systems aspects of surface and groundwater hydrology, hydrometeorology and hydrogeology. Relevant topics incorporating the insights and methodologies of disciplines such as climatology, water resource systems, hydraulics, agrohydrology, geomorphology, soil science, instrumentation and remote sensing, civil and environmental engineering are included. Social science perspectives on hydrological problems such as resource and ecological economics, environmental sociology, psychology and behavioural science, management and policy analysis are also invited. Multi-and interdisciplinary analyses of hydrological problems are within scope. The science published in the Journal of Hydrology is relevant to catchment scales rather than exclusively to a local scale or site.